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| DOE-STD-1128-98
Guide of Good Practices for Occupational Radiological Protection in Plutonium Facilities
detector geometry should be known when performing the primary calibration. Primary
calibration should be performed at least annually.
Standards referenced in Section 3.5.2 discuss specific performance testing of radiation
detection instruments. Testing procedures in these standards should be used for periodic
requalification of instruments or detailed testing of instruments.
The calibration of photon monitoring instruments over the energy range from a few keV to
300 keV is best accomplished with an x-ray machine and appropriate filters that provide
known x-ray spectra from a few kiloelectron volts to approximately 300 keV. Radionuclide
sources should be used for higher energies. Most ion chambers used to measure photon
typically used to calibrate these instruments. These sources also may be used to calibrate
Geiger-Mueller (GM) type detectors used for dose rate measurements. It should be noted
that some GM detectors (e.g., those with no energy compensation) can show a large energy
dependence, especially below approximately 200 keV. GM detectors should not be used if
not energy compensated.
241
Am, or 230Th sources. Several sources of different activities should be used to calibrate
different ranges.
Whenever possible, beta detectors should be calibrated to the beta energies of interest in the
workplace. A natural or depleted uranium slab source can be used for calibration of beta
detectors when beta radiations in the workplace have energies similar to the uranium.
International Organization for Standardization beta sources should be used for all other
purposes: the energy dependence of beta detectors can be tested using the calibration
sources listed in the ISO Publication 1980 (1984); these include 90Sr, 90Y, 204Tl, and 147Pm.
The calibration and testing of crucial monitoring systems are extremely important to the
overall radiation protection program but have often been neglected. Effluent monitoring and
sampling systems and remote area monitoring systems (RAMs) should be given several
tests. The radiological, environmental, and mechanical characteristics of the instrumentation
portion of the system should be fully evaluated prior to its first use to ensure its
compatibility with performance requirements and facility operating conditions. The effluent
sampling losses from the sample probe to the collector/detector should be determined. This
test should be repeated at least annually and when a significant change in the sampling
equipment is made. The sample probe should be examined at least once a year to verify that
its design or performance has not been changed by corrosion. The recorder of the sample
flow rate should be calibrated when it is installed and annually thereafter. The operability of
the overall system should be completely tested once, with repeat tests only after
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